Hazardous Waste Management System; Identification and Listing of Hazardous Waste, 42440-42447 [2018-17985]
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Dated: August 9, 2018.
Frank Brogan,
Assistant Secretary for Elementary and
Secondary Education.
§ 200.89
12. In § 200.89, amend the section
heading by removing the words ‘‘MEP
allocations;’’ and by removing and
reserving paragraph (a).
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For reasons discussed in the
preamble, and under the authority at 20
U.S.C. 3474, 20 U.S.C. 1221e–3, Public
Law 109–270, and Public Law 114–95,
the Secretary amends Chapter II of title
34 of the Code of Federal Regulations as
follows:
PART 200—TITLE I—IMPROVING THE
ACADEMIC ACHIEVEMENT OF THE
DISADVANTAGED
1. The authority citation for part 200
is revised to read as follows:
■
PART 237—[REMOVED AND
RESERVED]
■
13. Remove and reserve part 237.
PART 299—GENERAL PROVISIONS
14. The authority citation for part 299
continues to read as follows:
■
Authority: 20 U.S.C. 1221e–3(a)(1),
6511(a), and 7373(b), unless otherwise noted.
Subpart B—[Removed and Reserved]
Authority: 20 U.S.C. 6301 through 6576,
unless otherwise noted.
■
§ 200.7
[FR Doc. 2018–17480 Filed 8–21–18; 8:45 am]
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15. Remove and reserve subpart B,
consisting of § 299.3.
[Removed and Reserved]
2. Remove and reserve § 200.7.
§ 200.12
BILLING CODE 4000–01–P
[Removed and Reserved]
ENVIRONMENTAL PROTECTION
AGENCY
§§ 200.13 through 200.22
Reserved]
[EPA–R06–RCRA–2017–0556; FRL–9980–
07—Region 6]
[Removed and
4. Remove the center heading
‘‘Adequate Yearly Progress (AYP)’’ and
remove and reserve §§ 200.13 through
200.22.
■
§§ 200.27 and 200.28
Reserved]
5. Remove and reserve §§ 200.27 and
200.28.
■
[Removed and
6. Remove the center heading ‘‘LEA
and School Improvement’’ and remove
and reserve §§ 200.30 through 200.53.
■
7. Revise the center heading
‘‘Qualifications of Teachers and
Paraprofessionals’’ to read
‘‘Qualifications of Paraprofessionals’’.
■
§§ 200.55 through 200.57
Reserved]
■
[Removed and
8. Remove and reserve § 200.57.
§§ 200.59 and 200.60
Reserved]
[Removed and
9. Remove and reserve §§ 200.59 and
200.60.
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§ 200.80
■
[Removed and Reserved]
10. Remove and reserve § 200.80.
§ 200.81
[Amended]
11. In § 200.81, remove and reserve
paragraphs (d), (f), (g), and (h).
■
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40 CFR Part 261
Hazardous Waste Management
System; Identification and Listing of
Hazardous Waste
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
[Removed and
§§ 200.30 through 200.53
Reserved]
the requirements of hazardous waste
regulations under the Resource
Conservation and Recovery Act (RCRA)
when disposed of in Subtitle D landfills
but imposes testing conditions to ensure
that the future-generated wastes remain
qualified for delisting.
DATES: Effective August 22, 2018.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. EPA–R06–RCRA–2017–0556. All
documents in the docket are listed on
the https://www.regulations.gov website.
Although listed in the index, some
information is not publicly available,
e.g., CBI or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available electronically through https://
www.regulations.gov.
For
technical information regarding the
Blanchard Refinery petition, contact
Michelle Peace at 214–665–7430 or by
email at peace.michelle@epa.gov.
SUPPLEMENTARY INFORMATION: The
information in this section is organized
as follows:
FOR FURTHER INFORMATION CONTACT:
3. Remove the center heading ‘‘State
Accountability System’’ and remove and
reserve § 200.12.
■
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[Amended]
The Environmental Protection
Agency (EPA) is granting a petition
submitted by Blanchard Refining
Company LLC—(Blanchard) to exclude
(or delist) the residual solids generated
from the reclamation of oil bearing
hazardous secondary materials (OBSMs)
on-site at Blanchard’s Galveston Bay
Refinery (GBR), located in Texas City,
Texas from the lists of hazardous
wastes. EPA used the Delisting Risk
Assessment Software (DRAS) Version
3.0.35 in the evaluation of the impact of
the petitioned waste on human health
and the environment. The residual
solids are listed as F037 (primary oil/
water/solids separation sludge) when
they are reclaimed from the OBSMs.
After careful analysis and evaluation of
comments submitted by the public, the
EPA has concluded that the petitioned
wastes are not hazardous waste when
disposed of in Subtitle D landfills. This
exclusion applies to the residuals solids
generated at Blanchard’s Galveston Bay
Refinery (GBR), located in Texas City,
Texas facility. Accordingly, this final
rule excludes the petitioned waste from
SUMMARY:
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I. Overview Information
A. What action is EPA finalizing?
B. Why is EPA approving this delisting?
C. What are the limits of this exclusion?
D. How will Blanchard Refining manage
the waste if it is delisted?
E. When is the final delisting exclusion
effective?
F. How does this final rule affect states?
II. Background
A. What is a delisting?
B. What regulations allow facilities to
delist a waste?
C. What information must the generator
supply?
III. EPA’s Evaluation of the Waste Data
A. What waste and how much did
Blanchard petition EPA to delist?
B. How did Blanchard sample and analyze
the waste data in this petition?
IV. Public Comments Received on the
proposed exclusion
A. Who submitted comments on the
proposed rule?
B. Comments and Responses
V. Statutory and Executive Order Reviews
I. Overview Information
A. What action is EPA finalizing?
The EPA is finalizing:
(1) the decision to grant GBR’s
petition to have its surface
impoundment basin solids excluded, or
delisted, from the definition of a
hazardous waste, subject to certain
continued verification and monitoring
conditions; and
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(2) to use the Delisting Risk
Assessment Software to evaluate the
potential impact of the petitioned waste
on human health and the environment.
The Agency used this model to predict
the concentration of hazardous
constituents released from the
petitioned waste, once it is disposed.
After evaluating the petition, EPA
proposed rule, on October 31, 2017, to
exclude GBR’s residuals from the
treatment of OBSM waste from the lists
of hazardous wastes under §§ 261.31
and 261.32. The comments received on
this rulemaking will be addressed as
part of this decision.
B. Why is EPA approving this delisting?
GBR’s petition requests an exclusion
from the F037 waste listing pursuant to
40 CFR 260.20 and 260.22. GBR does
not believe that the petitioned waste
meets the criteria for which EPA listed
it. GBR also believes no additional
constituents or factors could cause the
waste to be hazardous. EPA’s review of
this petition included consideration of
the original listing criteria and the
additional factors required by the
Hazardous and Solid Waste
Amendments of 1984 (HSWA). See
section 3001(f) of RCRA, 42 U.S.C.
6921(f), and 40 CFR 260.22 (d)(1)
through (4) (hereinafter, all sectional
references are to 40 CFR unless
otherwise indicated). In making the
initial delisting determination, EPA
evaluated the petitioned waste against
the listing criteria and factors cited in
§ 261.11(a)(2) and (3). Based on this
review, EPA agrees with the petitioner
that the waste is non-hazardous with
respect to the original listing criteria. If
EPA had found, based on this review,
that the waste remained hazardous
based on the factors for which the waste
was originally listed, EPA would have
proposed to deny the petition. EPA
evaluated the waste with respect to
other factors or criteria to assess
whether there is a reasonable basis to
believe that such additional factors
could cause the waste to be hazardous.
EPA considered whether the waste is
acutely toxic, the concentration of the
constituents in the waste, their tendency
to migrate and to bioaccumulate, their
persistence in the environment once
released from the waste, plausible and
specific types of management of the
petitioned waste, the quantities of waste
generated, and waste variability. EPA
believes that the petitioned waste does
not meet the listing criteria and thus
should not be a listed waste. EPA’s
proposed decision to delist waste from
GBR is based on the information
submitted in support of this rule,
including descriptions of the wastes and
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analytical data from the Texas City,
Texas facility.
C. What are the limits of this exclusion?
This exclusion applies to the waste
described in the petition only if the
requirements described in Table 1 of
part 261, Appendix IX, and the
conditions contained herein are
satisfied. The exclusion applies to
20,000 cubic yards of residual solids.
D. How will Blanchard Refining manage
the waste if it is delisted?
Storage containers with OBSM
residual solids will be transported to an
authorized solid waste landfill (e.g.,
RCRA Subtitle D landfill, commercial/
industrial solid waste landfill, etc.) for
disposal.
E. When is the final delisting exclusion
effective?
This rule is effective August 22, 2018.
The Hazardous and Solid Waste
Amendments of 1984 amended Section
3010 of RCRA to allow rules to become
effective in less than six months when
the regulated community does not need
the six-month period to come into
compliance. That is the case here
because this rule reduces, rather than
increases, the existing requirements for
persons generating hazardous wastes.
These reasons also provide a basis for
making this rule effective immediately,
upon publication, under the
Administrative Procedure Act, pursuant
to 5 U.S.C. 553(d).
F. How does this final rule affect states?
Because EPA is issuing this exclusion
under the Federal RCRA delisting
program, only states subject to Federal
RCRA delisting provisions would be
affected. This would exclude two
categories of States: States having a dual
system that includes Federal RCRA
requirements and their own
requirements, and States who have
received our authorization to make their
own delisting decisions.
Here are the details: We allow states
to impose their own non-RCRA
regulatory requirements that are more
stringent than EPA’s, under section
3009 of RCRA. These more stringent
requirements may include a provision
that prohibits a federally issued
exclusion from taking effect in the State.
Because a dual system (that is, both
Federal (RCRA) and State (non-RCRA)
programs) may regulate a petitioner’s
waste, we urge petitioners to contact the
State regulatory authority to establish
the status of their wastes under the State
law.
EPA has also authorized some States
(for example, Louisiana, Georgia,
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Illinois) to administer a delisting
program in place of the Federal
program, that is, to make State delisting
decisions. Therefore, this exclusion
does not apply in those authorized
States. If Blanchard transports the
petitioned waste to or manages the
waste in any State with delisting
authorization, Blanchard must obtain
delisting authorization from that State
before they can manage the waste as
nonhazardous in the State.
II. Background
A. What is a delisting?
A delisting petition is a request from
a generator to EPA or another agency
with jurisdiction to exclude from the list
of hazardous wastes, wastes the
generator does not consider hazardous
under RCRA.
B. What regulations allow facilities to
delist a waste?
Under 40 CFR 260.20 and 260.22,
facilities may petition the EPA to
remove their wastes from hazardous
waste control by excluding them from
the lists of hazardous wastes contained
in §§ 261.31 and 261.32. Specifically,
§ 260.20 allows any person to petition
the Administrator to modify or revoke
any provision of parts 260 through 266,
268 and 273 of Title 40 of the Code of
Federal Regulations. Section 260.22
provides generators the opportunity to
petition the Administrator to exclude a
waste on a ‘‘generator-specific’’ basis
from the hazardous waste lists.
C. What information must the generator
supply?
Petitioners must provide sufficient
information to EPA to allow the EPA to
determine that the waste to be excluded
does not meet any of the criteria under
which the waste was listed as a
hazardous waste. In addition, the
Administrator must determine, where
he/she has a reasonable basis to believe
that factors (including additional
constituents) other than those for which
the waste was listed could cause the
waste to be a hazardous waste, that such
factors do not warrant retaining the
waste as a hazardous waste.
III. EPA’s Evaluation of the Waste Data
A. What waste and how much did
Blanchard petition EPA to delist?
In June 2017, Blanchard petitioned
EPA to exclude from the lists of
hazardous wastes contained in
§§ 261.31 and 261.32, residual solids
(F037) generated during reclamation
activities conducted at its GBR facility
located in Texas City, Texas. The waste
falls under the classification of listed
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waste pursuant to §§ 261.31 and 261.32.
Specifically, in its petition, Blanchard
requested that EPA grant a conditional
exclusion for the annual generation
volume of 20,000 cubic yards of F037
residual solids.
The 40 CFR part 261 Appendix VII
hazardous constituents which are the
basis for listing can be found in Table
1.
a 24-hour period of representative
TABLE 1—EPA WASTE CODES FOR
OBSM RESIDUAL SOLIDS AND THE operation. Each composite sample was
comprised of individual grab samples
BASIS FOR LISTING
Waste code
Basis for listing
F037 ...............
Benzene, benzo(a)pyrene,
chrysene, lead, chromium.
B. How did Blanchard sample and
analyze the waste data in this petition?
To support its petition, Blanchard
conducted individual sampling events
on residual solids resulting from the
reclamation of Blanchard’s three (3)
identified categories of OBSMs. Each
separate sampling event consisted of
four (4) composite samples taken during
(i.e., a minimum of four), obtained
during separate six (6) hour periods of
the 24-hour sampling event.
Compositing of samples and
performance of quality control
requirements were performed by
Blanchard’s selected analytical
laboratory, TestAmerica Laboratories,
Inc. (‘‘TestAmerica’’). Blanchard
submitted: Historical information on
waste generation and management
practices; and analytical results from
twelve samples for total and TCLP
concentrations of constituents of
concern (COC)s.
TABLE 2—ANALYTICAL RESULTS/MAXIMUM ALLOWABLE DELISTING CONCENTRATION RESIDUAL SOLIDS BLANCHARD
REFINING COMPANY LLC, TEXAS CITY, TEXAS
Maximum total
concentration
(mg/kg)
Constituent
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Acetone ......................................................................................................................
Antimony ....................................................................................................................
Anthracene .................................................................................................................
Arsenic .......................................................................................................................
Barium ........................................................................................................................
Benzene .....................................................................................................................
Benzo (a) anthracene ................................................................................................
Benzo(a) pyrene ........................................................................................................
Benzo (b) flouranthene ..............................................................................................
Beryllium ....................................................................................................................
Cadmium ....................................................................................................................
Chromium ..................................................................................................................
Chrysene ....................................................................................................................
Cobalt .........................................................................................................................
Copper .......................................................................................................................
Cyanide ......................................................................................................................
Diethyl Phthalate ........................................................................................................
Flouranthrene .............................................................................................................
Flourene .....................................................................................................................
Lead ...........................................................................................................................
2, methylphenol .........................................................................................................
3,4 methylphenol .......................................................................................................
Methylene Chloride ....................................................................................................
Methyl Naphthalene ...................................................................................................
Mercury ......................................................................................................................
Naphthalene ...............................................................................................................
Nickel .........................................................................................................................
Phenanthrene ............................................................................................................
Phenol ........................................................................................................................
Pyrene ........................................................................................................................
Pyridine ......................................................................................................................
Selenium ....................................................................................................................
Silver ..........................................................................................................................
Toluene ......................................................................................................................
Tin ..............................................................................................................................
Thallium .....................................................................................................................
Vanadium ...................................................................................................................
Zinc ............................................................................................................................
Maximum TCLP
concentration
(mg/L)
0.185
53.7
0.488
222.0
950.0
1.25
0.512
0.0298
0.286
8.61
0.441
120.0
0.272
242.0
639.0
99.4
0.493
0.405
0.420
963.0
1.31
2.18
0.827
0.365
0.0403
0.874
29,000
2.16
6.55
1.76
0.197
13.5
1.86
0.670
13.8
110.0
75, 400
1920.0
0.226
0.226
<0.0125
0.277
0.221
<0.00280
<0.0106
<0.0123
<0.0125
0.235
<0.00280
0.0550
<0.0103
0.818
<0.0813
<0.0702
<0.0130
<0.0122
<0.00710
<0.0219
<0.00710
<0.00675
0.00756
<0.0129
0.000104
<0.0110
<0.00800
<0.0112
0.00813
<0.0150
<0.0108
0.0530
<0.0129
<0.00275
<0.00590
0.0220
0.215
0.487
Maximum TCLP
delisting level
(mg/L)
520.0
0.599
25.993
0.424
36.0
0.077
0.070
2.634
22.43
1.764
0.217
3.06
7.006
0.902
21.527
3.08
990
2.462
4.91
0.984
28.952
28.952
0.0790
0.727
0.068
0.0327
13.5
10.626
173
4.446
0.5775
1.0
5.0
15.1
387
0.0366
4.6436
197
Notes: These levels represent the highest constituent concentration found in any one sample and does not necessarily represent the specific
level found in one sample.
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IV. Public Comments Received on the
Proposed Exclusion
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A. Who submitted comments on the
proposed rule?
The EPA received fifteen anonymous
public comments on the October 31,
2017, proposed rule via regulations.gov.
There were ten comments which had no
bearing on the delisting of hazardous
waste for Blanchard Refining. Two
comments: EPA–R06–RCRA–2017–
0556–0003 and EPA–R06–RCRA–2017–
0556–0005 were submitted in favor of
the issuance of the petition. Comments
and responses to the three adverse
comments (EPA–R06–RCRA–2017–
0556–0009) are addressed below.
B. Comments and Responses
General Comment: EPA Region 6
received ten comments through
regulations.gov to which no responses
are required. These comments are
numbered: EPA–R06–RCRA–2017–
0556–0002, EPA–R06–RCRA–2017–
0556–0004, EPA–R06–RCRA–2017–
0556–0006, EPA–R06–RCRA–2017–
0556–0007, EPA–R06–RCRA–2017–
0556–0009, EPA–R06–RCRA–2017–
0556–0010, EPA–R06–RCRA–2017–
0556–0011, EPA–R06–RCRA–2017–
0556–0012, EPA–R06–RCRA–2017–
0556–0013, and EPA–R06–RCRA–2017–
0556–0015 in this rulemaking docket.
These commenters expressed concerns
regarding wildfires, wind turbines,
climate change, car lithium batteries,
and opinions on Lead leaching into
drinking water which are not
appropriately addressed as part of the
Hazardous Waste delisting program.
Some comments reflect differences in
opinions or preferred outcomes, to
which an agency response is not
appropriate. The EPA acknowledges the
submission of these comments but notes
the comments are out of the scope of the
current final action regarding the
delisting of hazardous waste residuals
generated at Blanchard Refining.
Comment 1 (EPA–R06–RCRA–2017–
0556–0009): ‘‘I am writing in
representation of the over 150,000
members of TinyTimmy.org. We are
against delisting these Blanchard solid
hazardous wastes because they do not
meet the standards stated clearly by the
EPA for such delisting activity. Many of
their own test results show a much
higher than acceptable levels of some of
the most toxic chemicals known to man.
This attempt to delist byproducts such
as Appendix VII inorganic constituents
of concern, lead and chromium, and
Appendix VII organic constituents of
concern benzene, benzo(a)pyrene and
chrysene. The levels found by
Blanchard’s testing does not meet the
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EPA criteria for delistment. Further,
doing so violates human safety,
groundwater, environment and worker
health. We strongly urge the EPA to
reconsider and follow its actual mission
of protecting the health of both humans
and the environment and stop giving
out favors to the fossil fuel industry on
our backs.’’
Response 1 (EPA–R06–RCRA–2017–
0556–0009). The Delisting Program
requires extensive waste sampling and a
risk assessment is performed to assess a
wastes potential harm to human health
and the environment. The program is
designed to insure that the wastes
which are deemed excluded will not be
managed in a manner to harm human
health or the environment. This waste
will be managed in a Subtitle D
industrial waste landfill as solid waste
to prevent releases to groundwater and
air pathways.
Comment 2 (EPA–R06–RCRA–2017–
0556–0014). ‘‘I oppose the petition for
delisting and believe delisting would
pose a threat to the public.’’
Response 2 (EPA–R06–RCRA–2017–
0556–0014). The Delisting Program
requires extensive waste sampling and a
risk assessment is performed to assess a
wastes potential harm to human health
and the environment. The program is
designed to insure that the wastes
which are deemed excluded will not be
managed in a manner to harm human
health or the environment. This waste
will be managed in a Subtitle D
industrial waste landfill as solid waste
to prevent releases to groundwater and
air pathways.
Comment 3 (EPA–R06–RCRA–2017–
0556–0016). ‘‘I’d like to say thank you
for opportunity to comment. My
concern is regarding the delisting
mandate of the Blanchard Refinery
residual solid waste stream with
chemicals that are classifiable as known
carcinogenicity to human. The EPA is
basing the ruling on the results from
DRAS (Hazardous Waste Delisting Risk
Assessment Software). Per the EPA, ‘‘the
DRAS is a risk assessment tool and,
therefore, can only provide risk analyses
based on the information input into the
program.’’ Therefore, this software is not
a dynamic simulation of the site’s actual
contaminates level but rather a
‘‘subjective’’ user input simulation.
Also, the criteria for demonstration of
health-based levels is the Maximum
Toxicity Characteristic Leaching
Procedure (TCLP) delisting level. Does
this limit cover worksite exposure
limits? Will rate of evaporation affect
the TCLP concentration? If so, will there
be continuous monitoring at the site?
For example, Cobalt meets the
Maximum TCLP delisting level criteria
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of 0.902 (mg/L); however, per a New
Jersey Department of Health and Senior
Services Hazardous Substance Fact
Sheet, it does not meet the workplace
exposure limits.1
The average airborne permissible
exposure limits (PEL) according to:
OSHA: The legal PEL is 0.1 mg/m3 (8hour workshift)
NIOSH: The recommended PEL is 0.05
mg/m3 (10-hour workshift)
ACGIH: The legal PEL is 0.02 mg/m3 (8hour workshift)
Based on these limits, the maximum
TCLP is, using the most conservative
case, 900% higher. Also, according to
the same study, it is stated that cobalt
maybe a carcinogen in humans and
there may be no safe level of exposure
of exposure to a carcinogen.
Within the delisted chemicals, I have
identified multiple chemicals in
addition to Cobalt that are classifiable as
known carcinogenicity to human, such
as benzene and toluene. Since a landfill
is considered a worksite, the chemicals
should be reconsidered or the PEL
considered in the criteria for
demonstration of health-based levels.’’
Response 3 (EPA–R06–RCRA–2017–
0556–0016). The requirements of the
Federal regulations defined in 40 CFR
part 260.20, and 260.22, describe the
process by which wastes may be
removed from the list of hazardous
waste. In addition to extensive quality
assurance and quality control data for
the samples taken, EPA performs a risk
assessment using the Delisting Risk
Assessment Software to ensure that our
decision is protective of human health
and the environment. The constituent
concentrations found in the residual
solids are below the concentrations that
would pose harm to human health and
the environment. A waste is eligible for
delisting only if that waste, as generated
at a particular facility, does not meet
any of the criteria under which the
waste was listed as a hazardous waste.
In addition, the waste may not contain
any other Appendix VIII constituents
that would cause the waste to be
hazardous. RCRA § 3001(f) and 40 CFR
260.22. A delisting is only intended to
address a specific waste stream
generated at a specific site. Since
individual waste streams may vary
depending on raw materials, industrial
processes, and other factors, it may be
appropriate not to list a specific waste
from a specific site. Therefore, while a
waste described in the regulations or
resulting from the operation of the
mixture or derived-from rules generally
is hazardous, a specific waste from an
individual facility may not be
hazardous. For this reason, 40 CFR
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260.20 and 260.22 provide an exclusion
procedure, called delisting, which
allows persons to prove that EPA should
not regulate a specific waste from a
particular generating facility as a
hazardous waste. A risk assessment of
the petitioned waste is completed and is
a part of the decision factors in issuing
an exclusion. Specific health
examinations and worker protection are
covered by the facility operating plans
and overseen by OSHA. Worker safety
during the management of this waste to
avoid contact with this material are
covered by the Health and Safety plans
of the petitioner.
V. Statutory and Executive Order
Reviews
Under Executive Order 12866,
‘‘Regulatory Planning and Review’’ (58
FR 51735, October 4, 1993), this rule is
not of general applicability and
therefore, is not a regulatory action
subject to review by the Office of
Management and Budget (OMB). This
rule does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act of 1995
(44 U.S.C. 3501 et seq.) because it
applies to a particular facility only.
Because this rule is of particular
applicability relating to a particular
facility, it is not subject to the regulatory
flexibility provisions of the Regulatory
Flexibility Act (5 U.S.C. 601 et seq.), or
to sections 202, 204, and 205 of the
Unfunded Mandates Reform Act of 1995
(UMRA) (Pub. L. 104–4). Because this
rule will affect only a particular facility,
it will not significantly or uniquely
affect small governments, as specified in
section 203 of UMRA. Because this rule
will affect only a particular facility, this
rule does not have federalism
implications. It will not have substantial
direct effects on the States, on the
relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132, ‘‘Federalism’’,
(64 FR 43255, August 10, 1999). Thus,
Executive Order 13132 does not apply
to this rule. This action is considered an
Executive Order 13771 deregulatory
action. This final rule provides
meaningful burden reduction by
allowing the petitioner to manage an
estimated 20,000 cubic yards of residual
solids a year under RCRA Subtitle D
management standards rather than the
more stringent RCRA Subtitle C
standards. This action will significantly
reduce the costs associated with the onsite management, transportation and
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disposal of this wastestream by shifting
its management from RCRA Subtitle C
hazardous waste management to RCRA
Subtitle D nonhazardous waste
management.
Similarly, because this rule will affect
only a particular facility, this rule does
not have tribal implications, as specified
in Executive Order 13175,
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 9, 2000). Thus,
Executive Order 13175 does not apply
to this rule. This rule also is not subject
to Executive Order 13045, ‘‘Protection of
Children from Environmental Health
Risks and Safety Risks’’ (62 FR 19885,
April 23, 1997), because it is not
economically significant as defined in
Executive Order 12866, and because the
Agency does not have reason to believe
the environmental health or safety risks
addressed by this action present a
disproportionate risk to children. The
basis for this belief is that the Agency
used DRAS, which considers health and
safety risks to children, to calculate the
maximum allowable concentrations for
this rule. This rule is not subject to
Executive Order 13211, ‘‘Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355 (May
22, 2001)), because it is not a significant
regulatory action under Executive Order
12866. This rule does not involve
technical standards; thus, the
requirements of section 12(d) of the
National Technology Transfer and
Advancement Act of 1995 (15 U.S.C.
272 note) do not apply. As required by
section 3 of Executive Order 12988,
‘‘Civil Justice Reform’’, (61 FR 4729,
February 7, 1996), in issuing this rule,
EPA has taken the necessary steps to
eliminate drafting errors and ambiguity,
minimize potential litigation, and
provide a clear legal standard for
affected conduct.
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report which includes a
copy of the rule to each House of the
Congress and to the Comptroller General
of the United States. Section 804
exempts from section 801 the following
types of rules: (1) Rules of particular
applicability; (2) rules relating to agency
management or personnel; and (3) rules
of agency organization, procedure, or
practice that do not substantially affect
the rights or obligations of non-agency
parties (5 U.S.C. 804(3)). EPA is not
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required to submit a rule report
regarding this action under section 801
because this is a rule of particular
applicability. Executive Order (E.O.)
12898 (59 FR 7629 (Feb. 16, 1994))
establishes Federal executive policy on
environmental justice. Its main
provision directs Federal agencies, to
the greatest extent practicable and
permitted by law, to make
environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
EPA has determined that this rule will
not have disproportionately high and
adverse human health or environmental
effects on minority or low-income
populations because it does not affect
the level of protection provided to
human health or the environment. The
Agency’s risk assessment did not
identify risks from management of this
material in an authorized, solid waste
landfill (e.g. RCRA Subtitle D landfill,
commercial/industrial solid waste
landfill, etc.). Therefore, EPA believes
that any populations in proximity of the
landfills used by this facility should not
be adversely affected by common waste
management practices for this delisted
waste.
Lists of Subjects in 40 CFR Part 261
Environmental protection, Hazardous
Waste, Recycling, Reporting and recordkeeping requirements.
Authority: Sec. 3001(f) RCRA, 42 U.S.C.
6921(f).
Dated: July 31, 2018.
Wren Stenger,
Multimedia Division Director, Region 6.
For the reasons set out in the
preamble, 40 CFR part 261 is amended
as follows:
PART 261—IDENTIFICATION AND
LISTING OF HAZARDOUS WASTE
1. The authority citation for part 261
continues to read as follows:
■
Authority: 42 U.S.C. 6905, 6912(a), 6921,
6922, 6924(y) and 6938.
2. In Table 1 of Appendix IX to Part
261, add an entry for ‘‘Blanchard
Refining Company LLC’’ in alphabetical
order by facility to read as follows:
■
Appendix IX to Part 261—Waste
Excluded Under §§ 260.20 and 260.22
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TABLE 1—WASTES EXCLUDED FROM NON-SPECIFIC SOURCES
Facility
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Blanchard Refining Company LLC.
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Address
Waste description
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Texas City, TX ...................
*
*
*
*
Residual solids (EPA Hazardous Waste Numbers F037) generated at a maximum
rate of as 20,000 cubic yards annually.
For the exclusion to be valid, Blanchard must implement a verification testing program that meets the following Paragraphs:
(1) All leachable concentrations for those constituents must not exceed the following levels measured as mg/L (ppm). The petitioner must use an acceptable
leaching method, for example SW–846, Method 1311, to measure constituents in
the residual solids leachate:
(A) Inorganic Constituents of Concern: Antimony—0.5985; Arsenic—0.424; Barium—36; Beryllium—1.74; Chromium—3.06; Cobalt—0.902; Lead—0.984; Nickel—13.5; Selenium—1.0; Vanadium—4.64, Zinc—197. Mercury—0.068.
(B) Organic Constituents of Concern: Acetone—520.0; Anthracene—25.993; Benzene—0.077; Benzo(a)pyrene—2.634, Chrysene—7.006; Methylene Chloride—
0.0790; Phenanthrene—10.626; Phenol—173; Pyrene—4.446.
(2) Waste Holding and Handling:
(A) Blanchard must manage and dispose its residual solids as hazardous waste
generated under Subtitle C of RCRA, until they have completed verification testing described in Paragraph (3)(A) and (B), as appropriate, and valid analyses
show that paragraph (1) is satisfied.
(B) Levels of constituents measured in the samples of the residual solids that do
not exceed the levels set forth in Paragraph (1) are nonhazardous. Blanchard
can manage and dispose the nonhazardous residual solids according to all applicable solid waste regulations.
(C) If constituent levels in a sample exceed any of the delisting levels set in Paragraph (1), Blanchard must retreat or stabilize the residual solids represented by
the sample exceeding the delisting levels, until it meets the levels in paragraph
(1). Blanchard must repeat the analyses of the retreated residual solids.
(3) Verification Testing Requirements:
Blanchard must perform analytical testing by sampling and analyzing the Residual
solids as follows:
(i) Collect representative samples of the Residual solids for analysis of all constituents listed in paragraph (1) prior to disposal.
(ii) The samples for verification testing shall be a representative sample according
to appropriate methods. As applicable to the method-defined parameters of concern, analyses requiring the use of SW–846 methods incorporated by reference
in 40 CFR 260.11 must be used without substitution. As applicable, the SW–846
methods might include Methods 0010, 0011, 0020, 0023A, 0030, 0031, 0040,
0050, 0051, 0060, 0061, 1010A, 1020B, 1110A, 1310B, 1311, 1312, 1320,
1330A, 9010C, 9012B, 9040C, 9045D, 9060A, 9070A (uses EPA Method 1664,
Rev. A), 9071B, and 9095B. Methods must meet Performance Based Measurement System Criteria in which the Data Quality Objectives are to demonstrate
that samples of the Blanchard residual solids are representative for all constituents listed in paragraph (1).
Blanchard must perform sample collection and analyses, including quality control
procedures, according to SW–846 methodologies.
(A) Initial Verification Testing:
After EPA grants the final exclusion, Blanchard must do the following:
(i) Collect four (4) representative composite samples of the residual solids at weekly intervals after EPA grants the final exclusion. The first composite samples may
be taken at any time after EPA grants the final approval. Sampling should be
performed in accordance with the sampling plan approved by EPA in support of
the exclusion.
(ii) Analyze the samples for all constituents listed in paragraph (1). Any composite
sample taken that exceeds the delisting levels listed in paragraph (1) for the residual solids must be disposed as hazardous waste in accordance with the applicable hazardous waste requirements.
(iii) Within thirty (30) days after successfully completing its initial verification testing,
Blanchard may report its analytical test data for its initial four (4) weekly composite samples to EPA. If levels of constituents measured in the samples of the
residual solids do not exceed the levels set forth in paragraph (1) of this exclusion, Blanchard can manage and dispose the non-hazardous residual solids according to all applicable solid waste regulations.
(B) Subsequent Verification Testing:
If Blanchard completes initial verification testing requirements, specified in paragraph (3)(A), and no sample contains a constituent at a level which exceeds the
limits set forth in paragraph (1), Blanchard may begin subsequent verification
testing as follows:
(i) Blanchard must test representative composite samples of the residual solids for
all constituents listed in paragraph (1) at least once per month.
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TABLE 1—WASTES EXCLUDED FROM NON-SPECIFIC SOURCES—Continued
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Facility
Address
Waste description
(ii) The samples for the monthly testing shall be a representative composite sample
according to appropriate methods.
(iii) Within thirty (30) days after completing each monthly sampling, Blanchard will
report its analytical test data to EPA.
(C) Annual Verification Testing:
If levels of constituents measured in the samples of the residual solids do not exceed the levels set forth in paragraph (1) of this exclusion for six (6) consecutive
months of subsequent verification testing, Blanchard may begin annual testing as
follows:
(i) Blanchard must test representative composite samples of the residual solids for
all constituents listed in paragraph (1) at least once per calendar year.
(ii) The samples for the annual testing shall be a representative composite sample
according to appropriate methods.
(iii) Within sixty (60) days after completing each annual sampling, Blanchard will report its analytical test data to EPA.
(D) Termination of Organic Testing:
Blanchard must continue testing as required under Paragraph (3)(B) for organic
constituents in Paragraph (1)(B), until the analytical results submitted under
Paragraph (3)(B) show a minimum of three (3) consecutive monthly samples
below the delisting levels in Paragraph (1). Following receipt of approval from
EPA in writing, Blanchard may terminate organic testing.
(4) Changes in Operating Conditions:
If Blanchard significantly changes the process described in its petition or starts any
processes that generate(s) the waste that may or could affect the composition or
type of waste generated as established under Paragraph (1) (by illustration, but
not limitation, changes in equipment or operating conditions of the treatment
process), they must notify EPA in writing. Blanchard may no longer handle the
residual solids generated from the new process as nonhazardous until they have
completed verification testing described in Paragraph (3)(A) and (B), as appropriate, documented that valid analyses show that paragraph (1) is satisfied, and
received written approval from EPA.
(5) Stabilization Operation:
Blanchard may periodically elect to modify operating conditions to accommodate
the addition of chemical stabilization reagents during indirect thermal desorption
processing. In the event that Blanchard initiates the inclusion of stabilization during operation, they may no longer handle the residual solids generated from the
modified process as nonhazardous until the residual solids meet the delisting levels set in Paragraph (1) under initial verification testing requirements set in paragraph (3)(A) and verify that the stabilization reagents do not add additional constituents to the residual solid leachate. Following completion of modified operation, Blanchard can resume normal operating conditions and testing requirements under Paragraph (3), which were in place prior to initiating stabilization
during operation.
(6) Data Submittals:
Blanchard must submit the information described below. If Blanchard fails to submit
the required data within the specified time or maintain the required records onsite for the specified time, EPA, at its discretion, will consider this sufficient basis
to reopen the exclusion as described in paragraph (7). Blanchard must:
(A) Submit the data obtained through paragraph 3 to the Section Chief, 6MM–RP,
Multimedia Division, U.S. Environmental Protection Agency Region 6, 1445 Ross
Ave., Suite 1200, Dallas, Texas 75202, within the time specified. All supporting
data can be submitted on CD–ROM or comparable electronic media.
(B) Compile records of analytical data from paragraph (3), summarized, and maintained on-site for a minimum of five years.
(C) Furnish these records and data when either EPA or the State of Texas requests them for inspection.
(D) Send along with all data a signed copy of the following certification statement,
to attest to the truth and accuracy of the data submitted:
‘‘Under civil and criminal penalty of law for the making or submission of false or
fraudulent statements or representations (pursuant to the applicable provisions of
the Federal Code, which include, but may not be limited to, 18 U.S.C. 1001 and
42 U.S.C. 6928), I certify that the information contained in or accompanying this
document is true, accurate and complete.
As to the (those) identified section(s) of this document for which I cannot personally
verify its (their) truth and accuracy, I certify as the company official having supervisory responsibility for the persons who, acting under my direct instructions,
made the verification that this information is true, accurate and complete.
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TABLE 1—WASTES EXCLUDED FROM NON-SPECIFIC SOURCES—Continued
Facility
Address
Waste description
If any of this information is determined by EPA in its sole discretion to be false, inaccurate or incomplete, and upon conveyance of this fact to the company, I recognize and agree that this exclusion of waste will be void as if it never had effect
or to the extent directed by EPA and that the company will be liable for any actions taken in contravention of the company’s RCRA and CERCLA obligations
premised upon the company’s reliance on the void exclusion.’’
(7) Reopener:
(A) If, any time after disposal of the delisted waste Blanchard possesses or is otherwise made aware of any environmental data (including but not limited to
underflow water data or ground water monitoring data) or any other data relevant
to the delisted waste indicating that any constituent identified for the delisting
verification testing is at level higher than the delisting level allowed by the Division Director in granting the petition, then the facility must report the data, in writing, to the Division Director within 10 days of first possessing or being made
aware of that data.
(B) If either the verification testing (and retest, if applicable) of the waste does not
meet the delisting requirements in paragraph 1, Blanchard must report the data,
in writing, to the Division Director within 10 days of first possessing or being
made aware of that data.
(C) If Blanchard fails to submit the information described in paragraphs (6), (7)(A)
or (7)(B) or if any other information is received from any source, the Division Director will make a preliminary determination as to whether the reported information requires EPA action to protect human health and/or the environment. Further
action may include suspending, or revoking the exclusion, or other appropriate
response necessary to protect human health and the environment.
(D) If the Division Director determines that the reported information requires action
by EPA, the Division Director will notify the facility in writing of the actions the Division Director believes are necessary to protect human health and the environment. The notice shall include a statement of the proposed action and a statement providing the facility with an opportunity to present information as to why
the proposed EPA action is not necessary. The facility shall have 10 days from
receipt of the Division Director’s notice to present such information.
(E) Following the receipt of information from the facility described in paragraph
(7)(D) or (if no information is presented under paragraph (7)(D)) the initial receipt
of information described in paragraphs (6), (7)(A) or (7)(B), the Division Director
will issue a final written determination describing EPA actions that are necessary
to protect human health and/or the environment. Any required action described in
the Division Director’s determination shall become effective immediately, unless
the Division Director provides otherwise.
(8) Notification Requirements:
Blanchard must do the following before transporting the delisted waste. Failure to
provide this notification will result in a violation of the delisting petition and a possible revocation of the decision.
(A) Provide a one-time written notification to any state Regulatory Agency to which
or through which it will transport the delisted waste described above for disposal,
60 days before beginning such activities.
(B) For onsite disposal, a notice should be submitted to the State to notify the
State that disposal of the delisted materials has begun.
(C) Update one-time written notification, if it ships the delisted waste into a different
disposal facility.
(D) Failure to provide this notification will result in a violation of the delisting exclusion and a possible revocation of the decision.
*
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[FR Doc. 2018–17985 Filed 8–21–18; 8:45 am]
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Agencies
[Federal Register Volume 83, Number 163 (Wednesday, August 22, 2018)]
[Rules and Regulations]
[Pages 42440-42447]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-17985]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 261
[EPA-R06-RCRA-2017-0556; FRL-9980-07--Region 6]
Hazardous Waste Management System; Identification and Listing of
Hazardous Waste
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) is granting a
petition submitted by Blanchard Refining Company LLC--(Blanchard) to
exclude (or delist) the residual solids generated from the reclamation
of oil bearing hazardous secondary materials (OBSMs) on-site at
Blanchard's Galveston Bay Refinery (GBR), located in Texas City, Texas
from the lists of hazardous wastes. EPA used the Delisting Risk
Assessment Software (DRAS) Version 3.0.35 in the evaluation of the
impact of the petitioned waste on human health and the environment. The
residual solids are listed as F037 (primary oil/water/solids separation
sludge) when they are reclaimed from the OBSMs. After careful analysis
and evaluation of comments submitted by the public, the EPA has
concluded that the petitioned wastes are not hazardous waste when
disposed of in Subtitle D landfills. This exclusion applies to the
residuals solids generated at Blanchard's Galveston Bay Refinery (GBR),
located in Texas City, Texas facility. Accordingly, this final rule
excludes the petitioned waste from the requirements of hazardous waste
regulations under the Resource Conservation and Recovery Act (RCRA)
when disposed of in Subtitle D landfills but imposes testing conditions
to ensure that the future-generated wastes remain qualified for
delisting.
DATES: Effective August 22, 2018.
ADDRESSES: The EPA has established a docket for this action under
Docket ID No. EPA-R06-RCRA-2017-0556. All documents in the docket are
listed on the https://www.regulations.gov website. Although listed in
the index, some information is not publicly available, e.g., CBI or
other information whose disclosure is restricted by statute. Certain
other material, such as copyrighted material, is not placed on the
internet and will be publicly available only in hard copy form.
Publicly available docket materials are available electronically
through https://www.regulations.gov.
FOR FURTHER INFORMATION CONTACT: For technical information regarding
the Blanchard Refinery petition, contact Michelle Peace at 214-665-7430
or by email at [email protected].
SUPPLEMENTARY INFORMATION: The information in this section is organized
as follows:
I. Overview Information
A. What action is EPA finalizing?
B. Why is EPA approving this delisting?
C. What are the limits of this exclusion?
D. How will Blanchard Refining manage the waste if it is
delisted?
E. When is the final delisting exclusion effective?
F. How does this final rule affect states?
II. Background
A. What is a delisting?
B. What regulations allow facilities to delist a waste?
C. What information must the generator supply?
III. EPA's Evaluation of the Waste Data
A. What waste and how much did Blanchard petition EPA to delist?
B. How did Blanchard sample and analyze the waste data in this
petition?
IV. Public Comments Received on the proposed exclusion
A. Who submitted comments on the proposed rule?
B. Comments and Responses
V. Statutory and Executive Order Reviews
I. Overview Information
A. What action is EPA finalizing?
The EPA is finalizing:
(1) the decision to grant GBR's petition to have its surface
impoundment basin solids excluded, or delisted, from the definition of
a hazardous waste, subject to certain continued verification and
monitoring conditions; and
[[Page 42441]]
(2) to use the Delisting Risk Assessment Software to evaluate the
potential impact of the petitioned waste on human health and the
environment. The Agency used this model to predict the concentration of
hazardous constituents released from the petitioned waste, once it is
disposed.
After evaluating the petition, EPA proposed rule, on October 31,
2017, to exclude GBR's residuals from the treatment of OBSM waste from
the lists of hazardous wastes under Sec. Sec. 261.31 and 261.32. The
comments received on this rulemaking will be addressed as part of this
decision.
B. Why is EPA approving this delisting?
GBR's petition requests an exclusion from the F037 waste listing
pursuant to 40 CFR 260.20 and 260.22. GBR does not believe that the
petitioned waste meets the criteria for which EPA listed it. GBR also
believes no additional constituents or factors could cause the waste to
be hazardous. EPA's review of this petition included consideration of
the original listing criteria and the additional factors required by
the Hazardous and Solid Waste Amendments of 1984 (HSWA). See section
3001(f) of RCRA, 42 U.S.C. 6921(f), and 40 CFR 260.22 (d)(1) through
(4) (hereinafter, all sectional references are to 40 CFR unless
otherwise indicated). In making the initial delisting determination,
EPA evaluated the petitioned waste against the listing criteria and
factors cited in Sec. 261.11(a)(2) and (3). Based on this review, EPA
agrees with the petitioner that the waste is non-hazardous with respect
to the original listing criteria. If EPA had found, based on this
review, that the waste remained hazardous based on the factors for
which the waste was originally listed, EPA would have proposed to deny
the petition. EPA evaluated the waste with respect to other factors or
criteria to assess whether there is a reasonable basis to believe that
such additional factors could cause the waste to be hazardous. EPA
considered whether the waste is acutely toxic, the concentration of the
constituents in the waste, their tendency to migrate and to
bioaccumulate, their persistence in the environment once released from
the waste, plausible and specific types of management of the petitioned
waste, the quantities of waste generated, and waste variability. EPA
believes that the petitioned waste does not meet the listing criteria
and thus should not be a listed waste. EPA's proposed decision to
delist waste from GBR is based on the information submitted in support
of this rule, including descriptions of the wastes and analytical data
from the Texas City, Texas facility.
C. What are the limits of this exclusion?
This exclusion applies to the waste described in the petition only
if the requirements described in Table 1 of part 261, Appendix IX, and
the conditions contained herein are satisfied. The exclusion applies to
20,000 cubic yards of residual solids.
D. How will Blanchard Refining manage the waste if it is delisted?
Storage containers with OBSM residual solids will be transported to
an authorized solid waste landfill (e.g., RCRA Subtitle D landfill,
commercial/industrial solid waste landfill, etc.) for disposal.
E. When is the final delisting exclusion effective?
This rule is effective August 22, 2018. The Hazardous and Solid
Waste Amendments of 1984 amended Section 3010 of RCRA to allow rules to
become effective in less than six months when the regulated community
does not need the six-month period to come into compliance. That is the
case here because this rule reduces, rather than increases, the
existing requirements for persons generating hazardous wastes. These
reasons also provide a basis for making this rule effective
immediately, upon publication, under the Administrative Procedure Act,
pursuant to 5 U.S.C. 553(d).
F. How does this final rule affect states?
Because EPA is issuing this exclusion under the Federal RCRA
delisting program, only states subject to Federal RCRA delisting
provisions would be affected. This would exclude two categories of
States: States having a dual system that includes Federal RCRA
requirements and their own requirements, and States who have received
our authorization to make their own delisting decisions.
Here are the details: We allow states to impose their own non-RCRA
regulatory requirements that are more stringent than EPA's, under
section 3009 of RCRA. These more stringent requirements may include a
provision that prohibits a federally issued exclusion from taking
effect in the State. Because a dual system (that is, both Federal
(RCRA) and State (non-RCRA) programs) may regulate a petitioner's
waste, we urge petitioners to contact the State regulatory authority to
establish the status of their wastes under the State law.
EPA has also authorized some States (for example, Louisiana,
Georgia, Illinois) to administer a delisting program in place of the
Federal program, that is, to make State delisting decisions. Therefore,
this exclusion does not apply in those authorized States. If Blanchard
transports the petitioned waste to or manages the waste in any State
with delisting authorization, Blanchard must obtain delisting
authorization from that State before they can manage the waste as
nonhazardous in the State.
II. Background
A. What is a delisting?
A delisting petition is a request from a generator to EPA or
another agency with jurisdiction to exclude from the list of hazardous
wastes, wastes the generator does not consider hazardous under RCRA.
B. What regulations allow facilities to delist a waste?
Under 40 CFR 260.20 and 260.22, facilities may petition the EPA to
remove their wastes from hazardous waste control by excluding them from
the lists of hazardous wastes contained in Sec. Sec. 261.31 and
261.32. Specifically, Sec. 260.20 allows any person to petition the
Administrator to modify or revoke any provision of parts 260 through
266, 268 and 273 of Title 40 of the Code of Federal Regulations.
Section 260.22 provides generators the opportunity to petition the
Administrator to exclude a waste on a ``generator-specific'' basis from
the hazardous waste lists.
C. What information must the generator supply?
Petitioners must provide sufficient information to EPA to allow the
EPA to determine that the waste to be excluded does not meet any of the
criteria under which the waste was listed as a hazardous waste. In
addition, the Administrator must determine, where he/she has a
reasonable basis to believe that factors (including additional
constituents) other than those for which the waste was listed could
cause the waste to be a hazardous waste, that such factors do not
warrant retaining the waste as a hazardous waste.
III. EPA's Evaluation of the Waste Data
A. What waste and how much did Blanchard petition EPA to delist?
In June 2017, Blanchard petitioned EPA to exclude from the lists of
hazardous wastes contained in Sec. Sec. 261.31 and 261.32, residual
solids (F037) generated during reclamation activities conducted at its
GBR facility located in Texas City, Texas. The waste falls under the
classification of listed
[[Page 42442]]
waste pursuant to Sec. Sec. 261.31 and 261.32. Specifically, in its
petition, Blanchard requested that EPA grant a conditional exclusion
for the annual generation volume of 20,000 cubic yards of F037 residual
solids.
The 40 CFR part 261 Appendix VII hazardous constituents which are
the basis for listing can be found in Table 1.
Table 1--EPA Waste Codes for OBSM Residual Solids and the Basis for
Listing
------------------------------------------------------------------------
Waste code Basis for listing
------------------------------------------------------------------------
F037................................... Benzene, benzo(a)pyrene,
chrysene, lead, chromium.
------------------------------------------------------------------------
B. How did Blanchard sample and analyze the waste data in this
petition?
To support its petition, Blanchard conducted individual sampling
events on residual solids resulting from the reclamation of Blanchard's
three (3) identified categories of OBSMs. Each separate sampling event
consisted of four (4) composite samples taken during a 24-hour period
of representative operation. Each composite sample was comprised of
individual grab samples (i.e., a minimum of four), obtained during
separate six (6) hour periods of the 24-hour sampling event.
Compositing of samples and performance of quality control requirements
were performed by Blanchard's selected analytical laboratory,
TestAmerica Laboratories, Inc. (``TestAmerica''). Blanchard submitted:
Historical information on waste generation and management practices;
and analytical results from twelve samples for total and TCLP
concentrations of constituents of concern (COC)s.
Table 2--Analytical Results/Maximum Allowable Delisting Concentration Residual Solids Blanchard Refining Company
LLC, Texas City, Texas
----------------------------------------------------------------------------------------------------------------
Maximum total Maximum TCLP Maximum TCLP
Constituent concentration concentration delisting level
(mg/kg) (mg/L) (mg/L)
----------------------------------------------------------------------------------------------------------------
Acetone................................................ 0.185 0.226 520.0
Antimony............................................... 53.7 0.226 0.599
Anthracene............................................. 0.488 <0.0125 25.993
Arsenic................................................ 222.0 0.277 0.424
Barium................................................. 950.0 0.221 36.0
Benzene................................................ 1.25 <0.00280 0.077
Benzo (a) anthracene................................... 0.512 <0.0106 0.070
Benzo(a) pyrene........................................ 0.0298 <0.0123 2.634
Benzo (b) flouranthene................................. 0.286 <0.0125 22.43
Beryllium.............................................. 8.61 0.235 1.764
Cadmium................................................ 0.441 <0.00280 0.217
Chromium............................................... 120.0 0.0550 3.06
Chrysene............................................... 0.272 <0.0103 7.006
Cobalt................................................. 242.0 0.818 0.902
Copper................................................. 639.0 <0.0813 21.527
Cyanide................................................ 99.4 <0.0702 3.08
Diethyl Phthalate...................................... 0.493 <0.0130 990
Flouranthrene.......................................... 0.405 <0.0122 2.462
Flourene............................................... 0.420 <0.00710 4.91
Lead................................................... 963.0 <0.0219 0.984
2, methylphenol........................................ 1.31 <0.00710 28.952
3,4 methylphenol....................................... 2.18 <0.00675 28.952
Methylene Chloride..................................... 0.827 0.00756 0.0790
Methyl Naphthalene..................................... 0.365 <0.0129 0.727
Mercury................................................ 0.0403 0.000104 0.068
Naphthalene............................................ 0.874 <0.0110 0.0327
Nickel................................................. 29,000 <0.00800 13.5
Phenanthrene........................................... 2.16 <0.0112 10.626
Phenol................................................. 6.55 0.00813 173
Pyrene................................................. 1.76 <0.0150 4.446
Pyridine............................................... 0.197 <0.0108 0.5775
Selenium............................................... 13.5 0.0530 1.0
Silver................................................. 1.86 <0.0129 5.0
Toluene................................................ 0.670 <0.00275 15.1
Tin.................................................... 13.8 <0.00590 387
Thallium............................................... 110.0 0.0220 0.0366
Vanadium............................................... 75, 400 0.215 4.6436
Zinc................................................... 1920.0 0.487 197
----------------------------------------------------------------------------------------------------------------
Notes: These levels represent the highest constituent concentration found in any one sample and does not
necessarily represent the specific level found in one sample.
[[Page 42443]]
IV. Public Comments Received on the Proposed Exclusion
A. Who submitted comments on the proposed rule?
The EPA received fifteen anonymous public comments on the October
31, 2017, proposed rule via regulations.gov. There were ten comments
which had no bearing on the delisting of hazardous waste for Blanchard
Refining. Two comments: EPA-R06-RCRA-2017-0556-0003 and EPA-R06-RCRA-
2017-0556-0005 were submitted in favor of the issuance of the petition.
Comments and responses to the three adverse comments (EPA-R06-RCRA-
2017-0556-0009) are addressed below.
B. Comments and Responses
General Comment: EPA Region 6 received ten comments through
regulations.gov to which no responses are required. These comments are
numbered: EPA-R06-RCRA-2017-0556-0002, EPA-R06-RCRA-2017-0556-0004,
EPA-R06-RCRA-2017-0556-0006, EPA-R06-RCRA-2017-0556-0007, EPA-R06-RCRA-
2017-0556-0009, EPA-R06-RCRA-2017-0556-0010, EPA-R06-RCRA-2017-0556-
0011, EPA-R06-RCRA-2017-0556-0012, EPA-R06-RCRA-2017-0556-0013, and
EPA-R06-RCRA-2017-0556-0015 in this rulemaking docket. These commenters
expressed concerns regarding wildfires, wind turbines, climate change,
car lithium batteries, and opinions on Lead leaching into drinking
water which are not appropriately addressed as part of the Hazardous
Waste delisting program. Some comments reflect differences in opinions
or preferred outcomes, to which an agency response is not appropriate.
The EPA acknowledges the submission of these comments but notes the
comments are out of the scope of the current final action regarding the
delisting of hazardous waste residuals generated at Blanchard Refining.
Comment 1 (EPA-R06-RCRA-2017-0556-0009): ``I am writing in
representation of the over 150,000 members of TinyTimmy.org. We are
against delisting these Blanchard solid hazardous wastes because they
do not meet the standards stated clearly by the EPA for such delisting
activity. Many of their own test results show a much higher than
acceptable levels of some of the most toxic chemicals known to man.
This attempt to delist byproducts such as Appendix VII inorganic
constituents of concern, lead and chromium, and Appendix VII organic
constituents of concern benzene, benzo(a)pyrene and chrysene. The
levels found by Blanchard's testing does not meet the EPA criteria for
delistment. Further, doing so violates human safety, groundwater,
environment and worker health. We strongly urge the EPA to reconsider
and follow its actual mission of protecting the health of both humans
and the environment and stop giving out favors to the fossil fuel
industry on our backs.''
Response 1 (EPA-R06-RCRA-2017-0556-0009). The Delisting Program
requires extensive waste sampling and a risk assessment is performed to
assess a wastes potential harm to human health and the environment. The
program is designed to insure that the wastes which are deemed excluded
will not be managed in a manner to harm human health or the
environment. This waste will be managed in a Subtitle D industrial
waste landfill as solid waste to prevent releases to groundwater and
air pathways.
Comment 2 (EPA-R06-RCRA-2017-0556-0014). ``I oppose the petition
for delisting and believe delisting would pose a threat to the
public.''
Response 2 (EPA-R06-RCRA-2017-0556-0014). The Delisting Program
requires extensive waste sampling and a risk assessment is performed to
assess a wastes potential harm to human health and the environment. The
program is designed to insure that the wastes which are deemed excluded
will not be managed in a manner to harm human health or the
environment. This waste will be managed in a Subtitle D industrial
waste landfill as solid waste to prevent releases to groundwater and
air pathways.
Comment 3 (EPA-R06-RCRA-2017-0556-0016). ``I'd like to say thank
you for opportunity to comment. My concern is regarding the delisting
mandate of the Blanchard Refinery residual solid waste stream with
chemicals that are classifiable as known carcinogenicity to human. The
EPA is basing the ruling on the results from DRAS (Hazardous Waste
Delisting Risk Assessment Software). Per the EPA, ``the DRAS is a risk
assessment tool and, therefore, can only provide risk analyses based on
the information input into the program.'' Therefore, this software is
not a dynamic simulation of the site's actual contaminates level but
rather a ``subjective'' user input simulation.
Also, the criteria for demonstration of health-based levels is the
Maximum Toxicity Characteristic Leaching Procedure (TCLP) delisting
level. Does this limit cover worksite exposure limits? Will rate of
evaporation affect the TCLP concentration? If so, will there be
continuous monitoring at the site? For example, Cobalt meets the
Maximum TCLP delisting level criteria of 0.902 (mg/L); however, per a
New Jersey Department of Health and Senior Services Hazardous Substance
Fact Sheet, it does not meet the workplace exposure limits.1
The average airborne permissible exposure limits (PEL) according
to:
OSHA: The legal PEL is 0.1 mg/m3 (8-hour workshift)
NIOSH: The recommended PEL is 0.05 mg/m3 (10-hour workshift)
ACGIH: The legal PEL is 0.02 mg/m3 (8-hour workshift)
Based on these limits, the maximum TCLP is, using the most
conservative case, 900% higher. Also, according to the same study, it
is stated that cobalt maybe a carcinogen in humans and there may be no
safe level of exposure of exposure to a carcinogen.
Within the delisted chemicals, I have identified multiple chemicals
in addition to Cobalt that are classifiable as known carcinogenicity to
human, such as benzene and toluene. Since a landfill is considered a
worksite, the chemicals should be reconsidered or the PEL considered in
the criteria for demonstration of health-based levels.''
Response 3 (EPA-R06-RCRA-2017-0556-0016). The requirements of the
Federal regulations defined in 40 CFR part 260.20, and 260.22, describe
the process by which wastes may be removed from the list of hazardous
waste. In addition to extensive quality assurance and quality control
data for the samples taken, EPA performs a risk assessment using the
Delisting Risk Assessment Software to ensure that our decision is
protective of human health and the environment. The constituent
concentrations found in the residual solids are below the
concentrations that would pose harm to human health and the
environment. A waste is eligible for delisting only if that waste, as
generated at a particular facility, does not meet any of the criteria
under which the waste was listed as a hazardous waste. In addition, the
waste may not contain any other Appendix VIII constituents that would
cause the waste to be hazardous. RCRA Sec. 3001(f) and 40 CFR 260.22.
A delisting is only intended to address a specific waste stream
generated at a specific site. Since individual waste streams may vary
depending on raw materials, industrial processes, and other factors, it
may be appropriate not to list a specific waste from a specific site.
Therefore, while a waste described in the regulations or resulting from
the operation of the mixture or derived-from rules generally is
hazardous, a specific waste from an individual facility may not be
hazardous. For this reason, 40 CFR
[[Page 42444]]
260.20 and 260.22 provide an exclusion procedure, called delisting,
which allows persons to prove that EPA should not regulate a specific
waste from a particular generating facility as a hazardous waste. A
risk assessment of the petitioned waste is completed and is a part of
the decision factors in issuing an exclusion. Specific health
examinations and worker protection are covered by the facility
operating plans and overseen by OSHA. Worker safety during the
management of this waste to avoid contact with this material are
covered by the Health and Safety plans of the petitioner.
V. Statutory and Executive Order Reviews
Under Executive Order 12866, ``Regulatory Planning and Review'' (58
FR 51735, October 4, 1993), this rule is not of general applicability
and therefore, is not a regulatory action subject to review by the
Office of Management and Budget (OMB). This rule does not impose an
information collection burden under the provisions of the Paperwork
Reduction Act of 1995 (44 U.S.C. 3501 et seq.) because it applies to a
particular facility only. Because this rule is of particular
applicability relating to a particular facility, it is not subject to
the regulatory flexibility provisions of the Regulatory Flexibility Act
(5 U.S.C. 601 et seq.), or to sections 202, 204, and 205 of the
Unfunded Mandates Reform Act of 1995 (UMRA) (Pub. L. 104-4). Because
this rule will affect only a particular facility, it will not
significantly or uniquely affect small governments, as specified in
section 203 of UMRA. Because this rule will affect only a particular
facility, this rule does not have federalism implications. It will not
have substantial direct effects on the States, on the relationship
between the national government and the States, or on the distribution
of power and responsibilities among the various levels of government,
as specified in Executive Order 13132, ``Federalism'', (64 FR 43255,
August 10, 1999). Thus, Executive Order 13132 does not apply to this
rule. This action is considered an Executive Order 13771 deregulatory
action. This final rule provides meaningful burden reduction by
allowing the petitioner to manage an estimated 20,000 cubic yards of
residual solids a year under RCRA Subtitle D management standards
rather than the more stringent RCRA Subtitle C standards. This action
will significantly reduce the costs associated with the on-site
management, transportation and disposal of this wastestream by shifting
its management from RCRA Subtitle C hazardous waste management to RCRA
Subtitle D nonhazardous waste management.
Similarly, because this rule will affect only a particular
facility, this rule does not have tribal implications, as specified in
Executive Order 13175, ``Consultation and Coordination with Indian
Tribal Governments'' (65 FR 67249, November 9, 2000). Thus, Executive
Order 13175 does not apply to this rule. This rule also is not subject
to Executive Order 13045, ``Protection of Children from Environmental
Health Risks and Safety Risks'' (62 FR 19885, April 23, 1997), because
it is not economically significant as defined in Executive Order 12866,
and because the Agency does not have reason to believe the
environmental health or safety risks addressed by this action present a
disproportionate risk to children. The basis for this belief is that
the Agency used DRAS, which considers health and safety risks to
children, to calculate the maximum allowable concentrations for this
rule. This rule is not subject to Executive Order 13211, ``Actions
Concerning Regulations That Significantly Affect Energy Supply,
Distribution, or Use'' (66 FR 28355 (May 22, 2001)), because it is not
a significant regulatory action under Executive Order 12866. This rule
does not involve technical standards; thus, the requirements of section
12(d) of the National Technology Transfer and Advancement Act of 1995
(15 U.S.C. 272 note) do not apply. As required by section 3 of
Executive Order 12988, ``Civil Justice Reform'', (61 FR 4729, February
7, 1996), in issuing this rule, EPA has taken the necessary steps to
eliminate drafting errors and ambiguity, minimize potential litigation,
and provide a clear legal standard for affected conduct.
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report which includes a copy of the rule to
each House of the Congress and to the Comptroller General of the United
States. Section 804 exempts from section 801 the following types of
rules: (1) Rules of particular applicability; (2) rules relating to
agency management or personnel; and (3) rules of agency organization,
procedure, or practice that do not substantially affect the rights or
obligations of non-agency parties (5 U.S.C. 804(3)). EPA is not
required to submit a rule report regarding this action under section
801 because this is a rule of particular applicability. Executive Order
(E.O.) 12898 (59 FR 7629 (Feb. 16, 1994)) establishes Federal executive
policy on environmental justice. Its main provision directs Federal
agencies, to the greatest extent practicable and permitted by law, to
make environmental justice part of their mission by identifying and
addressing, as appropriate, disproportionately high and adverse human
health or environmental effects of their programs, policies, and
activities on minority populations and low-income populations in the
United States.
EPA has determined that this rule will not have disproportionately
high and adverse human health or environmental effects on minority or
low-income populations because it does not affect the level of
protection provided to human health or the environment. The Agency's
risk assessment did not identify risks from management of this material
in an authorized, solid waste landfill (e.g. RCRA Subtitle D landfill,
commercial/industrial solid waste landfill, etc.). Therefore, EPA
believes that any populations in proximity of the landfills used by
this facility should not be adversely affected by common waste
management practices for this delisted waste.
Lists of Subjects in 40 CFR Part 261
Environmental protection, Hazardous Waste, Recycling, Reporting and
record-keeping requirements.
Authority: Sec. 3001(f) RCRA, 42 U.S.C. 6921(f).
Dated: July 31, 2018.
Wren Stenger,
Multimedia Division Director, Region 6.
For the reasons set out in the preamble, 40 CFR part 261 is amended
as follows:
PART 261--IDENTIFICATION AND LISTING OF HAZARDOUS WASTE
0
1. The authority citation for part 261 continues to read as follows:
Authority: 42 U.S.C. 6905, 6912(a), 6921, 6922, 6924(y) and
6938.
0
2. In Table 1 of Appendix IX to Part 261, add an entry for ``Blanchard
Refining Company LLC'' in alphabetical order by facility to read as
follows:
Appendix IX to Part 261--Waste Excluded Under Sec. Sec. 260.20 and
260.22
[[Page 42445]]
Table 1--Wastes Excluded From Non-Specific Sources
----------------------------------------------------------------------------------------------------------------
Facility Address Waste description
----------------------------------------------------------------------------------------------------------------
* * * * * * *
Blanchard Refining Company LLC.......... Texas City, TX............. Residual solids (EPA Hazardous Waste
Numbers F037) generated at a maximum
rate of as 20,000 cubic yards annually.
For the exclusion to be valid, Blanchard
must implement a verification testing
program that meets the following
Paragraphs:
(1) All leachable concentrations for
those constituents must not exceed the
following levels measured as mg/L (ppm).
The petitioner must use an acceptable
leaching method, for example SW-846,
Method 1311, to measure constituents in
the residual solids leachate:
(A) Inorganic Constituents of Concern:
Antimony--0.5985; Arsenic--0.424;
Barium--36; Beryllium--1.74; Chromium--
3.06; Cobalt--0.902; Lead--0.984;
Nickel--13.5; Selenium--1.0; Vanadium--
4.64, Zinc--197. Mercury--0.068.
(B) Organic Constituents of Concern:
Acetone--520.0; Anthracene--25.993;
Benzene--0.077; Benzo(a)pyrene--2.634,
Chrysene--7.006; Methylene Chloride--
0.0790; Phenanthrene--10.626; Phenol--
173; Pyrene--4.446.
(2) Waste Holding and Handling:
(A) Blanchard must manage and dispose its
residual solids as hazardous waste
generated under Subtitle C of RCRA,
until they have completed verification
testing described in Paragraph (3)(A)
and (B), as appropriate, and valid
analyses show that paragraph (1) is
satisfied.
(B) Levels of constituents measured in
the samples of the residual solids that
do not exceed the levels set forth in
Paragraph (1) are nonhazardous.
Blanchard can manage and dispose the
nonhazardous residual solids according
to all applicable solid waste
regulations.
(C) If constituent levels in a sample
exceed any of the delisting levels set
in Paragraph (1), Blanchard must retreat
or stabilize the residual solids
represented by the sample exceeding the
delisting levels, until it meets the
levels in paragraph (1). Blanchard must
repeat the analyses of the retreated
residual solids.
(3) Verification Testing Requirements:
Blanchard must perform analytical testing
by sampling and analyzing the Residual
solids as follows:
(i) Collect representative samples of the
Residual solids for analysis of all
constituents listed in paragraph (1)
prior to disposal.
(ii) The samples for verification testing
shall be a representative sample
according to appropriate methods. As
applicable to the method-defined
parameters of concern, analyses
requiring the use of SW-846 methods
incorporated by reference in 40 CFR
260.11 must be used without
substitution. As applicable, the SW-846
methods might include Methods 0010,
0011, 0020, 0023A, 0030, 0031, 0040,
0050, 0051, 0060, 0061, 1010A, 1020B,
1110A, 1310B, 1311, 1312, 1320, 1330A,
9010C, 9012B, 9040C, 9045D, 9060A, 9070A
(uses EPA Method 1664, Rev. A), 9071B,
and 9095B. Methods must meet Performance
Based Measurement System Criteria in
which the Data Quality Objectives are to
demonstrate that samples of the
Blanchard residual solids are
representative for all constituents
listed in paragraph (1).
Blanchard must perform sample collection
and analyses, including quality control
procedures, according to SW-846
methodologies.
(A) Initial Verification Testing:
After EPA grants the final exclusion,
Blanchard must do the following:
(i) Collect four (4) representative
composite samples of the residual solids
at weekly intervals after EPA grants the
final exclusion. The first composite
samples may be taken at any time after
EPA grants the final approval. Sampling
should be performed in accordance with
the sampling plan approved by EPA in
support of the exclusion.
(ii) Analyze the samples for all
constituents listed in paragraph (1).
Any composite sample taken that exceeds
the delisting levels listed in paragraph
(1) for the residual solids must be
disposed as hazardous waste in
accordance with the applicable hazardous
waste requirements.
(iii) Within thirty (30) days after
successfully completing its initial
verification testing, Blanchard may
report its analytical test data for its
initial four (4) weekly composite
samples to EPA. If levels of
constituents measured in the samples of
the residual solids do not exceed the
levels set forth in paragraph (1) of
this exclusion, Blanchard can manage and
dispose the non-hazardous residual
solids according to all applicable solid
waste regulations.
(B) Subsequent Verification Testing:
If Blanchard completes initial
verification testing requirements,
specified in paragraph (3)(A), and no
sample contains a constituent at a level
which exceeds the limits set forth in
paragraph (1), Blanchard may begin
subsequent verification testing as
follows:
(i) Blanchard must test representative
composite samples of the residual solids
for all constituents listed in paragraph
(1) at least once per month.
[[Page 42446]]
(ii) The samples for the monthly testing
shall be a representative composite
sample according to appropriate methods.
(iii) Within thirty (30) days after
completing each monthly sampling,
Blanchard will report its analytical
test data to EPA.
(C) Annual Verification Testing:
If levels of constituents measured in the
samples of the residual solids do not
exceed the levels set forth in paragraph
(1) of this exclusion for six (6)
consecutive months of subsequent
verification testing, Blanchard may
begin annual testing as follows:
(i) Blanchard must test representative
composite samples of the residual solids
for all constituents listed in paragraph
(1) at least once per calendar year.
(ii) The samples for the annual testing
shall be a representative composite
sample according to appropriate methods.
(iii) Within sixty (60) days after
completing each annual sampling,
Blanchard will report its analytical
test data to EPA.
(D) Termination of Organic Testing:
Blanchard must continue testing as
required under Paragraph (3)(B) for
organic constituents in Paragraph
(1)(B), until the analytical results
submitted under Paragraph (3)(B) show a
minimum of three (3) consecutive monthly
samples below the delisting levels in
Paragraph (1). Following receipt of
approval from EPA in writing, Blanchard
may terminate organic testing.
(4) Changes in Operating Conditions:
If Blanchard significantly changes the
process described in its petition or
starts any processes that generate(s)
the waste that may or could affect the
composition or type of waste generated
as established under Paragraph (1) (by
illustration, but not limitation,
changes in equipment or operating
conditions of the treatment process),
they must notify EPA in writing.
Blanchard may no longer handle the
residual solids generated from the new
process as nonhazardous until they have
completed verification testing described
in Paragraph (3)(A) and (B), as
appropriate, documented that valid
analyses show that paragraph (1) is
satisfied, and received written approval
from EPA.
(5) Stabilization Operation:
Blanchard may periodically elect to
modify operating conditions to
accommodate the addition of chemical
stabilization reagents during indirect
thermal desorption processing. In the
event that Blanchard initiates the
inclusion of stabilization during
operation, they may no longer handle the
residual solids generated from the
modified process as nonhazardous until
the residual solids meet the delisting
levels set in Paragraph (1) under
initial verification testing
requirements set in paragraph (3)(A) and
verify that the stabilization reagents
do not add additional constituents to
the residual solid leachate. Following
completion of modified operation,
Blanchard can resume normal operating
conditions and testing requirements
under Paragraph (3), which were in place
prior to initiating stabilization during
operation.
(6) Data Submittals:
Blanchard must submit the information
described below. If Blanchard fails to
submit the required data within the
specified time or maintain the required
records on-site for the specified time,
EPA, at its discretion, will consider
this sufficient basis to reopen the
exclusion as described in paragraph (7).
Blanchard must:
(A) Submit the data obtained through
paragraph 3 to the Section Chief, 6MM-
RP, Multimedia Division, U.S.
Environmental Protection Agency Region
6, 1445 Ross Ave., Suite 1200, Dallas,
Texas 75202, within the time specified.
All supporting data can be submitted on
CD-ROM or comparable electronic media.
(B) Compile records of analytical data
from paragraph (3), summarized, and
maintained on-site for a minimum of five
years.
(C) Furnish these records and data when
either EPA or the State of Texas
requests them for inspection.
(D) Send along with all data a signed
copy of the following certification
statement, to attest to the truth and
accuracy of the data submitted:
``Under civil and criminal penalty of law
for the making or submission of false or
fraudulent statements or representations
(pursuant to the applicable provisions
of the Federal Code, which include, but
may not be limited to, 18 U.S.C. 1001
and 42 U.S.C. 6928), I certify that the
information contained in or accompanying
this document is true, accurate and
complete.
As to the (those) identified section(s)
of this document for which I cannot
personally verify its (their) truth and
accuracy, I certify as the company
official having supervisory
responsibility for the persons who,
acting under my direct instructions,
made the verification that this
information is true, accurate and
complete.
[[Page 42447]]
If any of this information is determined
by EPA in its sole discretion to be
false, inaccurate or incomplete, and
upon conveyance of this fact to the
company, I recognize and agree that this
exclusion of waste will be void as if it
never had effect or to the extent
directed by EPA and that the company
will be liable for any actions taken in
contravention of the company's RCRA and
CERCLA obligations premised upon the
company's reliance on the void
exclusion.''
(7) Reopener:
(A) If, any time after disposal of the
delisted waste Blanchard possesses or is
otherwise made aware of any
environmental data (including but not
limited to underflow water data or
ground water monitoring data) or any
other data relevant to the delisted
waste indicating that any constituent
identified for the delisting
verification testing is at level higher
than the delisting level allowed by the
Division Director in granting the
petition, then the facility must report
the data, in writing, to the Division
Director within 10 days of first
possessing or being made aware of that
data.
(B) If either the verification testing
(and retest, if applicable) of the waste
does not meet the delisting requirements
in paragraph 1, Blanchard must report
the data, in writing, to the Division
Director within 10 days of first
possessing or being made aware of that
data.
(C) If Blanchard fails to submit the
information described in paragraphs (6),
(7)(A) or (7)(B) or if any other
information is received from any source,
the Division Director will make a
preliminary determination as to whether
the reported information requires EPA
action to protect human health and/or
the environment. Further action may
include suspending, or revoking the
exclusion, or other appropriate response
necessary to protect human health and
the environment.
(D) If the Division Director determines
that the reported information requires
action by EPA, the Division Director
will notify the facility in writing of
the actions the Division Director
believes are necessary to protect human
health and the environment. The notice
shall include a statement of the
proposed action and a statement
providing the facility with an
opportunity to present information as to
why the proposed EPA action is not
necessary. The facility shall have 10
days from receipt of the Division
Director's notice to present such
information.
(E) Following the receipt of information
from the facility described in paragraph
(7)(D) or (if no information is
presented under paragraph (7)(D)) the
initial receipt of information described
in paragraphs (6), (7)(A) or (7)(B), the
Division Director will issue a final
written determination describing EPA
actions that are necessary to protect
human health and/or the environment. Any
required action described in the
Division Director's determination shall
become effective immediately, unless the
Division Director provides otherwise.
(8) Notification Requirements:
Blanchard must do the following before
transporting the delisted waste. Failure
to provide this notification will result
in a violation of the delisting petition
and a possible revocation of the
decision.
(A) Provide a one-time written
notification to any state Regulatory
Agency to which or through which it will
transport the delisted waste described
above for disposal, 60 days before
beginning such activities.
(B) For onsite disposal, a notice should
be submitted to the State to notify the
State that disposal of the delisted
materials has begun.
(C) Update one-time written notification,
if it ships the delisted waste into a
different disposal facility.
(D) Failure to provide this notification
will result in a violation of the
delisting exclusion and a possible
revocation of the decision.
* * * * * * *
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[FR Doc. 2018-17985 Filed 8-21-18; 8:45 am]
BILLING CODE 6560-50-P